Distinct Leishmania species infecting wild caviomorph rodents (Rodentia: Hystricognathi) from Brazil.

BACKGROUND: Caviomorph rodents, some of the oldest Leishmania spp. hosts, are widely dispersed in Brazil. Despite both experimental and field studies having suggested that these rodents are potential reservoirs of Leishmania parasites, not more than 88 specimens were analyzed in the few studies of natural infection. Our hypothesis was that caviomorph rodents are inserted in the transmission cycles of Leishmania in different regions, more so than is currently recognized.
METHODOLOGY: We investigated the Leishmania infection in spleen fragments of 373 caviomorph rodents from 20 different species collected in five Brazilian biomes in a period of 13 years. PCR reactions targeting kDNA of Leishmania sp. were used to diagnose infection, while Leishmania species identification was performed by DNA sequencing of the amplified products obtained in the HSP70 (234) targeting. Serology by IFAT was performed on the available serum of these rodents. PRINCIPAL
FINDINGS: In 13 caviomorph rodents, DNA sequencing analyses allowed the identification of 4 species of the subgenus L. (Viannia): L. shawi, L. guyanensis, L. naiffi, and L. braziliensis; and 1 species of the subgenus L. (Leishmania): L. infantum. These include the description of parasite species in areas not previously included in their known distribution: L. shawi in Thrichomys inermis from Northeastern Brazil and L. naiffi in T. fosteri from Western Brazil. From the four other positive rodents, two were positive for HSP70 (234) targeting but did not generate sequences that enabled the species identification, and another two were positive only in kDNA targeting.
CONCLUSIONS/SIGNIFICANCE: The infection rate demonstrated by the serology (51.3%) points out that the natural Leishmania infection in caviomorph rodents is much higher than that observed in the molecular diagnosis (4.6%), highlighting that, in terms of the host species responsible for maintaining Leishmania species in the wild, our current knowledge represents only the "tip of the iceberg."

Introduction

More than 30 species within the Leishmania genus (Trypanosomatidae, Trypanosomatida) are recognized, including both extremely specific as well as generalist species transmitted by a variety of Phlebotomine vectors worldwide [1]–[2] In fact, several Leishmania species are multi-host parasites that infect mammal species of different orders, including humans [3]–[4]. The diversity of Leishmania species, mammal hosts and environments in which the transmission occurs reveals a complex system. Leishmaniasis has an important impact on public health since it results in a spectrum of debilitating diseases, which can progress to very severe, even fatal cases. In Brazil, human cutaneous leishmaniasis is associated with at least six different species of the subgenus Leishmania (Viannia) besides Leishmania (Leishmania) amazonensis, while the visceral form is exclusively associated with Leishmania (L.) infantum [5]–[7].

Although usually interpreted as such, the description of Leishmania DNA in a given mammal species is not sufficient to consider this species a reservoir host. Reservoir is better defined not as a single species, but as an assemblage of species responsible for the long lasting maintenance of a parasite in a given environment [8]. In reservoir systems, each species of mammal host plays a unique role in the maintenance of the parasite, which means that these systems should always be considered in a restricted spatio-temporal scale, particular to each site and each moment [9]. Failures in interrupting human transmission and preventing new epidemics are probably related to the lack of knowledge of various aspects of the natural transmission cycles of these parasites. In this sense, the involvement of synanthropic hosts, such as caviomorph rodents and their potential to act as reservoirs cannot be ignored.

Although the diagnosis of Leishmania sp. infection in mammal tissues through molecular assays has been conducted by several groups, the identification of the Leishmania species is still a great challenge [10]–[12]. The parasite isolation in wild mammals is complex to due to the difficulties in performing aseptic culture during field expeditions. Besides, the usually observed low parasite load and irregular distribution of parasites among host tissues impair even more the isolation efficiency [13]–[17]. To overcome such limitations, molecular approaches have been developed and applied aiming to detect and identify Leishmania species directly in biological samples. The advantage of molecular approaches based on PCR is that they combine high sensitivity for direct detection of the infecting parasites in various human, animal and sand fly tissues, with species specificity [18]. The PCR followed by either Restriction Fragment Polymorphism (RFLP) or DNA sequencing of distinct targets have already been employed in biological samples. Not all of them are, however, useful for identification at the species level. Molecular targets directed to the conserved region of the kinetoplast minicircles of Leishmania are the most used for diagnosis due to their sensitivity (which is related to the high number of copies in a single parasite (∼10.000) but detects only the subgenerum level. The PCR-RFLP of the internal transcribed spacer 1 (ITS1) is the assay commonly used for direct detection and identification of Leishmania species in the Old World, but for Brazilian species presents a lower resolution. Among the targets that result in intraspecific variability, the Heat Shock Protein of 70 kDa is encoded by a polymorphic gene which has regions allowing diagnosis of the Leishmania species circulating in Brazil [19].

Rodents comprise more than two hundred species distributed in many different habitats. In fact, in nature, we found semi-aquatic, terrestrial and semi-fossorial species [20]. This trait is probably the main reason explaining their exposure to the different transmission cycles of several species of Leishmania in the wild [8]. The South American rodents are divided into two sub orders (Sciurognathi and Hystricognathi). The first Caviomorph rodents (Rodentia: Hystricognathi) arrived in the Americas about 35mya (million years ago), much earlier than other rodent groups [21]. Along with the first caviomorph migrants, during the Oligocene, it has already been proposed that new species of the Leishmania (Leishmania) subgenus may have arrived and subsequently diversified in the native mammal fauna [22].

Nowadays, caviomorph rodents are widely distributed in Brazil and contribute significantly to the animal biomass of these habitats. They are also found in peridomestic environments that report the circulation of Leishmania parasites among other species of mammals, humans and/or dogs [23]–[26]. To date in Brazil, there are few studies of natural Leishmania infection in caviomorph rodents and not more than 88 specimens were analyzed [27]–[29]. Furthermore, experimental studies pointed to the putative role of two caviomorph species as Leishmania reservoirs: Thrichomys laurentius infected by L. infantum and L. braziliensis [17] and Proechimys semispinosus infected with L. infantum [30]. In this sense, the analysis of different caviomorph rodent species from different regions and collected at different periods of time, may define the role of these taxa in the reservoir host system of Leishmania sp. In the present study we investigate the infection by Leishmania spp. in 373 caviomorph rodents from 20 different species and discuss the role of this group in the maintenance of the transmission cycles of Leishmania spp. in different regions of Brazil.

Materials and Methods

Animal samples

We evaluated spleen fragments from caviomorph rodents (n = 373) collected in five out six Brazilian biomes between 1999 and 2012 (S1 Table). These animals were captured using Tomahawk and Shermann “live-traps” during studies conducted by our laboratory [31]–[33]. In these studies, whenever the euthanasia of animals were realized, usually for taxonomic identification and/or diagnosis of parasite's infection, spleen fragments were collected in plastic tubes containing ethanol and stored at −20°C.

Molecular diagnosis

All tissue fragments were re-hydrated with Nuclease-free water and the DNA extraction was performed using the Wizard Genomic DNA Purification Kit (Promega, Madison, USA) according to the manufacturer's recommendations. Positive and negative controls were derived from fragments of spleen and liver from infected (Leishmania braziliensis–IOC-L2483) and non-infected hamsters provided by the animal facilities of the Oswaldo Cruz Foundation. PCR were conducted using the pureTaq Ready-To-Go PCR beads (Amersham Biosciences, Buckinghamshire, UK) and primers directed to the conserved region of the Leishmania -kDNA minicircle, as follows: forward: 5′ – GGGAGGGGCGTTCTGCGAA-3′ and reverse: 5′ – GGCCCACTAT ATTACACCAACCCC – 3′ [17]. The PCR products were visualized after electrophoresis on 8% polyacrylamide gel and silver staining using a specific kit (DNA Silver Staining, GE Healthcare). Positive samples were submitted to a new PCR directed to a fragment of 234 bp of the hsp70 gene, using the following primers (5′ - GGA CGA GAT CGA GCG CAT GGT - 3′) and (5′- TCC TTC GAC GCC TCC TGG TTG - 3′) [19]. The PCR amplifications were performed in a final volume of 50 µL containing 5 µL of DNA, 0.2 pmol of each primer, 0.2 µM dNTPs, 1.5 mM MgCl2 and 1 U GoTaq®DNA polymerase (Promega). The PCR assays used the following amplification cycle: 94°C for 5 min followed by 30 cycles of 94°C for 30 sec, 63°C for 1 min and 72°C for 1 min and a final extension at 72°C for 10 min. To increase the number of DNA copies, products obtained in the first reaction were submitted to a second PCR with the same primers and conditions described.

The PCR products obtained for HSP70 (234) targeting and the products positive only in kDNA targeting were purified using the Wizard SV Gel kit and PCR Clean-up System kit (Promega). The both products were sequenced with the same primers used for the PCR assay using the ABI PRISM BigDyeTerminator v3.1 Cycle Sequencing Kit. Sequencing was performed on an automated DNA sequencer (ABI PRISM®BigDye™ Terminator Cycle Sequencing) at the Genomic Platform – DNA Sequencing (PDTIS – FIOCRUZ). Consensus sequences were aligned and edited with the BioEdit Version v7.1.11 [34] and Phred/Phrap/Consed package Version: 0.020425.c [35] from two forward and two reverse strands. Sequences with Phred values below ten over their extent were discarded and only sequence segments with values above twenty were used for contig construction. Contigs from all samples were manually assembled and aligned in MEGA4 [36]. For that samples that not generated good-quality consensus sequence, the PCR reaction and the DNA sequencing was repeated two or more times until we obtain sequence segments equal to the previously established criteria. Species identification was performed by similarity analysis obtained by Alignment Search Tool (BLAST) algorithm hosted by NCBI, National Institute of Health, USA (http://www.ncbi.nlm.nih.gov), against sequences available on GeneBank after calculation of the statistical significance of matches. Besides, we also compared our sequences with a panel of sequences for HSP70 (234) gene obtained from representative strains of different Leishmania species circulating in Brazil available in the Leishmania collection of the Oswaldo Cruz Institute/CLIOC (Table 1). This table was allowed the identification of the positions of the polymorphic site that differentiates the parasite species.

Table 1

Main polymorphisms along the HSP70 (234) sequences that allow the distinction of Leishmania species from reference strains.

Leishmania Species	Position of Polymorphyc Site
	19	22	23	24	35	36	39	45	47	48	58	70	78	79	113	116	117	122	145	148	150	156	158	160	161	163	168	170	171	174	181	182	183	185	201
L. (V) braziliensis	T	G	T	C	C	A	C	A	A	T	G	G	G	T	G	G	C	A	G	G	G	G	A	C	G	G	A	T	C	C	C	A	C	G	A
L. (V) shawi	.	.	.	.	.	.	.	.	.	.	.	.	.	.	A	.	.	.	.	.	.	.	G	.	.	.	.	.	.	.	.	G	.	.	.
L. (V) guyanenis	.	.	.	.	.	.	.	.	.	.	.	.	.	.	A	.	.	.	.	.	.	.	.	.	.	.	.	.	.	.	.	.	.	.	.
L. (V) naiffi	.	.	.	.	.	.	.	.	.	.	.	.	.	C	.	.	.	.	.	.	.	.	.	.	A	.	C	.	.	.	.	G	.	.	.
L. (V) lainsoni	.	.	.	.	.	.	.	.	.	.	.	.	C	.	A	T	.	.	.	.	.	A	G	.	.	.	.	.	.	.	.	.	.	.	.
L. (L) infantum	C	.	A	T	G	C	A	G	G	C	C	A	.	C	C	.	G	T	C	T	.	A	G	.	A	.	.	A	A	A	.	G	T	A	G
L. (L) amazonensis	C	A	A	T	G	C	A	.	G	C	C	A	.	.	C	.	G	T	C	C	C	A	T	G	A	A	.	A	A	A	G	G	.	.	G

Serological diagnosis

The immunofluorescence assay (IFAT) was performed on 130 available serum samples from the evaluated rodents, as described by Camargo (1966) [37]. A mixture of promastigotes from cultures of L. (V.) braziliensis (IOC/L566) and L. (L.) infantum (IOC/L579) obtained from CLIOC was used as antigen. In order to detect possible cross-reaction with Trypanosoma cruzi, sera were also tested using reference strains of T. cruzi (TcI M000/BR/1974/F and TcII MHOM/BR/1950/Y). The reactions were conducted using an in-house intermediary antibody anti-Thrichomys serum produced in rabbits [38]. The reaction was visualized using a commercial anti-rabbit IgG-FITC (Sigma-Aldrich, St. Louis, USA). Rodents that displayed serological titers 1/10 and 1/20 for Leishmania spp. infection were considered positive only if these titers were equal or higher than the titers observed in the same rodent for T. cruzi infection. Rodents that displayed Leishmania serological titers equal or higher than 1∶40 were considered positive independent of T. cruzi results.

Ethics statement

All the procedures carried out with these animals were authorized by the Brazilian Institute of Environment and Renewable Natural Resources (IBAMA) and followed protocols approved by the Ethics Committee of Animal Use Fiocruz (P0007-99, P0179-03; P0292/06; L0015-07).

Results

We found 17 caviomorph rodents (4.6%) positive in the PCR directed to Leishmania sp. kDNA. From these, 15 samples were also positive when tested for HSP70 (234) primers, two directly after the PCR and 13 only after the re-amplification of the product obtained in the first PCR reaction (Fig. 1). DNA sequencing analyses allowed the identification of −4 species of the subgenus Leishmania (Viannia) and −1 species of the subgenus Leishmania (Leishmania) in samples of 13 caviomorph rodents (Fig. 2, Table 2). In five situations, the DNA sequence analysis revealed identity values above 95% for more than one Leishmania species and we opted not to define one of them as the etiological agent. A single sample (one Thrichomys laurentius from Piauí) displayed different DNA sequences that presented high values of similarity with distinct species of Leishmania in two consecutive reactions. This was considered as result of a hybrid population or mixed infection. Leishmania infection was observed in five caviomorph rodent species captured in two municipalities belonging to Pantanal and in two belonging to Caatinga biomes (Fig. 2). In the Pantanal, 7 animals were positive for Leishmania spp and the identification of the Leishmania species was possible in 4 of them: one T. fosteri captured in Corumbá, was found infected by L. (V). naiffi while L. (L). infantum was found infecting one Dasyprocta azarae and two Clyomys laticeps in Aquidauna and Corumbá, respectively. Also in Corumbá, we were unable to identify the Leishmania species infecting one T. fosteri because the analysis of the parasite DNA sequence revealed similarity with two Leishmania species (L. (V). naiffi and L. (V). braziliensis).

Figure 1

Illustrative representation of HSP 70 (234) amplification for Leishmania sp. before and after re-amplification of the PCR products.

(A) PCR products of first amplification of HSP 70 (234) targeting analyzed by electrophoresis polyacrylamide gel stained with silver. Lanes: bp. molecular-weight marker (50 bp DNA ladder); 1. Infected Thrichomys laurentius from São Raimundo Nonato/PI; 2. Negative control of PCR reaction. (B) PCR products of re-amplification of the product obtained in the first PCR reaction. Lanes: bp. molecular-weight marker (50 bp DNA ladder); 1. Negative Thrichomys fosteri from Corumbá/MS (Positive only in kDNA); 2–5. Infected T. laurentius from São Raimundo Nonato/PI; 6. Infected T. fosteri from Corumbá/MS; 7. Negative control of PCR after re-amplification.

Figure 2

Map of the distribution of Leishmania species infecting caviomorph rodents in Brazil.

Blue markers indicate municipalities where caviomorph rodents were collected, but were all negative in the molecular assay. Red markers indicate municipalities with animals positive for Leishmania infection. * Sample with high value between distinct species of Leishmania was considered as a result of hybrid or mixed infection.

Table 2

Infected caviomorph rodents and their respective Leishmania species identified by the analysis of similarity between the DNA sequences from the PCR products targeting HSP70 (234) and available sequences from GeneBank.

Locality	Positive mammal	Leishmania identification	Max Score	Identity (%)
Bahia	Thrichomys inermis	Leishmania (V). shawi	422	99
Mato Grosso do Sul	Thrichomys fosteri	Leishmaia (V). naiffi	390	99
	Dasyprocta azarae	Leishmania (L). infantum	185	88
	Clyomys laticeps	Leishmania (L). infantum	427	99
	Clyomys laticeps	Leishmania (L). infantum	361	93
	Thrichomys fosteri	Leishmaia (V). naiffi OR	435	100
		Leishmania (V). braziliensis	424	99
Piauí	Thrichomys laurentius	Leishmania (V). guyanensis	433	100
	Thrichomys laurentius	Leishmania (L). infantum	303	97
	Thrichomys laurentius	Leishmania (V). braziliensis OR	422	99
		Leishmaia (V). naiffi	422	99
	Thrichomys laurentius	Leishmania (V). shawi OR	390	95
		Leishmania (V). guyanensis	385	95
	Thrichomys laurentius	Leishmaia (V). naiffi OR	435	100
		Leishmania (V). braziliensis	424	99
	Thrichomys laurentius	Leishmaia (V). naiffi OR	422	99
		Leishmania (V). braziliensis	411	98
	Thrichomys laurentius *	Leishmania (V). guyanensis	416	100
		Leishmania (V). braziliensis	416	99

* Sample with high value between distinct species of Leishmania was considered as a result of hybrid or mixed infection.

From Caatinga biome, in the municipality of Curacá/Bahia, one Thrichomys inermis was found infected by L. (V). shawi. In São Raimundo Nonato/Piauí, two T. laurentius were found infected, respectively, by L. (V). guyanensis and L. (L.) infantum. In four T. laurentius, the identification of the Leishmania species was not possible because the parasite DNA sequencing analyses showed high similarity for two Leishmania species (Table 2). The specific diagnosis in the seventh T. laurentius was only possible after two attempts and showed the presence of two Leishmania species, L. (V). braziliensis and L. (V). guyanensis (S2 Table). This was interpreted as the result of a mixed infection and/or a possible hybrid of them.

The prevalence of antibodies against Leishmania sp. in IFAT was 51.3% (59/115). In 15 samples the results were inconclusive and were therefore not included in the final analysis. Among the samples analyzed (S1 Table), 56 animals were positive in IFAT but negative by PCR. From these, the majority of them (n = 34) displayed titers equal or higher than 1∶20 in the IFAT. Of the six animals positive for Leishmania kDNA, three were also positive by IFAT. Other 53 rodents were negative for both tests.

Discussion

A clear expansion of leishmaniasis around the country has been observed in the last decades [23], [39]–[41]. From the different reasons already proposed to explain this expansion, a common point is the recognition that we still have poor knowledge of some aspects of the biology and epidemiology of Leishmania species, which, in the end, result in inefficient control strategies. The mammalian hosts of most Leishmania species are still poorly understood, which reinforces the need for studies that verify the distribution of these parasites in other mammalian taxa beyond those classically reported as reservoirs. Caviomorph rodents comprise an enormous group of species that exploit different habitats, and also include some species already domesticated by humans, such as the chinchilla and the guinea pig (Cavia spp.) [42].

Among the rodent species found infected in this study, only species from genus Dazyprocta and Thrichomys were already found infected by Leishmania spp. in Brazil. Dasyprocta sp., was found infected by L. guyanensis in Pará state [27] while T. apereoides, was founded infected by L. braziliensis, L. guyanensis, and L. amazonensis in Minas Gerais state [28]–[29]. Morevoer, other Thrichomys species were reported as potential reservoirs of trypanosome species in different regions of Brazil [33], [43]. We presented here the first description of Leishmania infection in Clyomys laticeps, a rodent species already found naturally infected by T. evansi and T. cruzi in Pantanal region” [33], [44].

Thrichomys inermis was the most abundant small mammal captured during the field expedition in Curaçá/Bahia, which points to its importance as a potential reservoir host. We described here for the first time, L. shawi in rodents, as well as this Leishmania species outside the Amazon region. Up to know, L. shawi is known to be transmitted only by Lutzomyia whitmani associated to arboreal and/or scansorial mammals (primates, sloths and coatis) suggesting a transmission cycle restricted to this forest strata [7], [45]. In a first view, our findings led to the suggestion that this transmission could also occur near the ground, since T. inermis is a terrestrial rodent that only rarely explores the understory strata [20]. However, we recently revealed through camera traps another species of this genus (T. fosteri) invading a coati nest about 12 meters high in the Pantanal region (Guilherme Mourão, personal communication). This finding reflects the lack of knowledge about the biology of some of the most widely distributed mammal species and the risk of incorrectly interpreting the parasite transmission cycle based on misconceptions of the biology of their mammal hosts and/or vectors.

American visceral leishmaniasis (AVL) is widely distributed in the state of Mato Grosso do Sul. Currently, the Aquidauana municipality displays an increasing number of human and canine cases in the urban area [46] and here we report for the first time the presence of L. infantum in sylvatic areas of this municipality. It is worth mentioning that although Dazypropcta azarae is a wild rodent species, these animals are frequently found in urban environments such as parks and woodlands. In these localities, these animals have no natural predators and are usually provided with food by local visitors, resulting in propitious conditions for reproduction. The presence of synanthropic L. infantum hosts in areas of intense transmission is a factor usually not considered in the epidemiology of VL. Nevertheless, we can not rule out the participation of other wild hosts in this transmission cycle, which is a complicating factor for the success of control strategies.

Also in the Pantanal region, the Corumbá municipality is endemic for AVL, recording dog's and human's cases [47]–[48]. In this municipality, there were conducted four expeditions between 2003 and 2009, and Leishmania infected rodents were found in all of them. The captures occurred in two farms that present different land uses. The Alegria Farm has livestock activities whereas the Nhumirim Farm is the center for scientific studies and presents large conservation areas. Two Clyomys laticeps, each one captured in one farm were found infected by L. infantum. This is especially important in the Alegria Farm where the interaction between wild and domestic mammals is common. All other infected rodents were captured in the Nhumirim Farm, pointing out that richness of biodiversity, as encountered in preserved areas, also reflect parasite diversity. At least one Thrichomys fosteri were found infected by Leishmania naiffi and this represents the first description of Leishmania naiffi in rodents and also of this Leishmania species outside the Amazon region [49]–[50]. Although we found no reports of the known L. naiffi vectors in the Mato Grosso do Sul state, their presence cannot be discarded or, alternatively, this transmission is being maintained by other phlebotomine species [51]. Another T. fosteri was founded infected by L. naiffi although the sequence of the amplified products revealed that L. braziliensis could not be discarded as etiologic agent of this infection. Indeed, these species differ in solely four nitrogenous bases at positions 79, 161, 168 e 182 when sequenced to target HSP70 (234) (Table 1).

Our data from São Raimundo Nonato/Piauí revealed the higher diversity of Leishmania species in a single host species, Thrichomys laurentius. This diversity could be observed in two consecutive years of expeditions. T. laurentius are a wild mammal species that has synanthropic habits and displayed high relative abundance in both expeditions. These rodents displayed high prevalence of infection that can potentially be considered a risk of infection not only for other wildlife populations, but also for domestic animals and men that expose themselves in areas of transmission. One T. laurentius was found infected by L. infantum. Indeed, the Piauí state is endemic for AVL with records of infection in marsupials, dogs and wild carnivores [52]–[55]. Another T. laurentius was found infected by L. guyanensis. This parasite species is commonly found in the Amazon region and known to be transmitted mainly by Lutzomyia umbratilis, a anthropophilic species that is generally found in understory strata [56].

Despite the difficulties, specific diagnosis is crucial to better understand the complex network of transmission of Leishmania species, which was achieved in the above mentioned situations. Ideally, studies that focus on the description of Leishmania reservoirs in a given area should be performed in long-termed studies. When not possible, punctual studies may also be quite informative, but it is imperative that this must to be analysed within a broad methodological approach that includes parasitological, serological and molecular diagnoses in different tissues. These factors will define the role of a given mammal host as a reservoir of Leishmania parasites. Nevertheless, this study design not always is possible due to inherent difficulties in working with wild mammals in the field. The molecular algorithm proposed here sought to combine the sensitivity of a molecular target and the specificity of DNA sequencing analysis of a locus. In fact, PCR targeted to the conserved region of kDNA has proved to be the most sensitive, but only allows the identification up to the subgenus level [15], [57]. Although less sensitive to diagnose the infection, the variable region of HSP 70 enabled the identification of the parasite species [19]. It is worth mentioning that in most cases positive reactions were only visualized after the re-amplification of the sequences obtained in the first reaction. This is the first time this approach is applied directly in tissue samples from wild mammals.

Also in São Raimundo Nonato, the analysis of the molecular identification of four animals resulted in similar sequences for more than one Leishmania species. One T. laurentius showed similar results for L. shawi and L. guyanensis, an expected result since both Leishmania species belong to the same complex and differ only in two bases, in HSP70 (234) sequence (Table 1). Other three T. laurentius showed similar results for L. braziliensis e L. naiffi (Table 2). We also obtained a divergent result after repeating the PCR reaction of one T. laurentius sample, which was interpreted as a result of a mixed infection or a hybrid between L. braziliensis and L. guyanensis. These five situations of inconclusive species identification reflect an inherent limitation of the employed methodology. On the other hand, it highlights how complex the identification of Leishmania species is (especially when sylvatic samples are used) and reflects how challenging is the establishment of a universal methodology, unique for diagnosis of the infection. In nature, the evolutionary success of Leishmania populations depends on their ability to multiply and be transmitted in different microenvironments (vertebrate and invertebrate hosts), which are both influenced by the habitat where they live. This process of evolution species is a dynamic, mutable and still poorly known phenomenon. Our attempt to describe the parasitic populations resulting from such complex interactions into discrete (not continuous) taxonomic units, although epidemiologically important, is always subject to findings like these. These should not be interpreted as an indicative to search for new discriminatory molecular markers, but instead as a natural report of the complexity that exists in Leishmania taxa.

The serological survey showed that 51.3% of the caviomorph rodents evaluated had become exposed to Leishmania parasites, and, therefore, are expected to be infected. However, we found only 4.6% of positive rodents through the molecular analysis of spleen fragments. Leishmania sp. has non-uniform distribution in tissues of vertebrate hosts, and may be present in other fragments of the spleen as well as in different tissues as skin and/or liver. The three animals that were positive for the molecular diagnosis, but negative for IFAT may have been caught in an initial phase of infection when there was not yet production of detectable IgG in serological tests. Another factor, although less known in wild hosts, may be an inability (permanent or temporary) of some individuals to produce detectable antibodies in serological assays. The rate of infection demonstrated by the serology points out that the natural Leishmania infection in caviomorph rodents is much higher than that observed in the molecular diagnosis. Our results based on PCR of spleen fragments and serology reflects only the “tip of the iceberg” highlighting that the knowledge about the epidemiology of different Leishmania species that infect caviomorph rodents is just at its beginning. The diversity of Leishmania species found infecting different caviomorph rodent species reflects the dynamism and complexity of the transmission cycles of these parasites in nature.

Origin of the analyzed caviomorph rodents, which were collected in Brazil between 1999 and 2012.

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Similarity levels observed by BLAST analysis among the DNA sequencing obtained for the target HSP70 (234) in the infected caviomorph rodents and available sequences from GeneBank with their respective accession numbers.

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